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The Prevention of Environmental Damage in Time of Armed Conflict: Proportionality and Precautionary Measures1

Published online by Cambridge University Press:  17 February 2009

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The law of war historically paid scant attention to the protection of the environment. Its main focus was to regulate hostilities so as protect combatants from unnecessary injury. Since World War II, it has turned to the protection of the civilian population and individual civilians. It does not follow that the environment did not receive any protection at all. In as much as international humanitarian law places constraints on the use of means and methods of warfare, the environment was indirectly protected. Thus, the provisions of the Hague or the Geneva Conventions, through the protection of civilian property and objects, offer indirect protection of the environment. Similarly, the banning of weapons of mass destruction, such as biological and chemical weapons, or the restraints on activities related to nuclear warfare, such as the testing of nuclear weapons, also ultimately limit potential damage to the environment caused by armed conflicts.

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Copyright © T.M.C. Asser Instituut and the Authors 2000

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References

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22. A ‘modernized’ version of the Martens Clause appears in Art. 1(2) AP I:

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‘In effect, the Martens Clause provided authority for treating the principles of humanity and the dictates of public conscience as principles of international law, leaving the precise content of the standard implied by these principles of international law to be ascertained in the light of changing conditions, inclusive of changes in the means and methods of warfare and the outlook and tolerance levels of the international community. The principles would remain constant, but their practical effect would vary from time to time: they could justify a method of warfare in one age and prohibit it in another.’

Dissenting Opinion of Judge Shahabuddeen, pp. 153 at 160.

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32. UN Doc. A/C.6/46/SR.18, para. 14.

33. M.N. Schmitt, ‘War and the Environment: Fault Lines in the Prescriptive Landscape’, in Austin and Bruch, op. cit. n. 3, pp. 87–136 at 97.

34. See for instance the Final Report to the Prosecutor by the Committee Established to Review the NATO Bombing Campaign Against the Federal Republic of Yugoslavia (2000) (hereafter, ‘OTP Report’), paras. 18–25, where the Committee applied the concept of environmental collateral damage.

35. Legality of the Threat or Use of Nuclear Weapons, supra n. 23, para. 30, see also para. 33.

36. OTP Report, supra n. 34, para. 18.

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47. NATO spokesperson as quoted in the BTF Report, supra n. 45, p. 33.

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51. Legality of the Threat or Use of Nuclear Weapons, supra n. 23, para. 29.

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63. Classical international law rested on the theory that all treaty relations between belligerents were severed by the outbreak of hostilities. A concurrent view has been the maintenance of treaty relationships, except for those the performance of which would be manifestly incompatible with a state of war, for instance, treaties of friendship and trade or treaties of alliance. See in general, Delbrück, J., ‘War, Effects on Treaties’, in Bernhardt, R., ed., Encyclopedia of Public International Law, Vol. 4 (Amsterdam, North-Holland 1982) pp. 310315Google Scholar; McNair, A., The Law of Treaties (Oxford, Clarendon Press 1961) pp. 695728Google Scholar.

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66. Some conventions do take into consideration the effect of hostilities either implicitly or explicitly, or cover military activities, although these are rather the exception than the rule. Some conventions explicitly allow for their suspension in case of war or other hostilities (e.g., International Convention for the Prevention of Pollution of the Sea by Oil (1954), Article XIX (but it was superseded by the MARPOL Convention (1973/1978) which does not contain such a provision)); others exclude military activities or objects from their scope of application. Treaties that establish civil liability regimes generally exclude compensation for damage occurring as a result of war of armed conflict. Other conventions do not explicitly cover military activities but states have agreed to apply the provisions applicable to such activities as far as practicable: Convention on the Prevention of Marine Pollution by Dumping of Wastes and Other Matter (1972), Article VII; Vienna Convention on Early Notification of a Nuclear Accident (1986). See Shaw, M.N., International Law, 4th edn. (Cambridge, Cambridge University Press 1997) p. 622Google Scholar; United Nations Convention on the Law of the Sea, 7 October 1982, UN Doc. A/CONF.62/122 and Corr., Article 236; Heintschel von Heinegg and Donner, loc. cit. n. 60, at p. 299.

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68. Protection of the environment in times of armed conflict, supra n. 19, para. 56. Also, Report of the Secretary-General on the protection of the environment in times of armed conflict, UN Doc. A/48/269 (29 July 1993), at p. 15, para. 76.

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72. Report of the Secretary-General on the protection of the environment in times of armed conflict, supra n. 18, p. 7, para. 34.

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78. Art. 36, AP I.

79. Szasz, loc. cit. n. 69, at p. 282.

80. Tarasofsky, loc. cit. n. 38, at p. 74.

81. UNEP Governing Council, Resolution 16/11B of 31 May 1991, para. 2.

82. Supra n. 30, p. 222, n. 110.

83. Rio Declaration (1992) supra n. 26, Principle 18; ILA Montreal Rules of International Law Applicable to Transfrontier Pollution (1982) Art. 7; United Nations Convention on the Law of the Sea (1982) supra n. 66, Art. 198; Convention on Early Notification of Nuclear Accidents, Vienna, 26 September 1986, reprinted in 25 ILM (1986) p. 1370Google Scholar, Art. 1; Convention on Biological Diversity, Rio de Janeiro, 5 June 1992, reprinted in 31 ILM (1992) p. 822, Art. 14Google Scholar.

84. Kiss, A., ‘Activités scientifiques et techniques et devoir d'information en droit international’, in Droits et liberiés à la fin du XXe siècle. Influence des données économiques et technologiques: Etudes offertes à Claude-Albert Colliard (Paris, Pedone 1984) pp. 273288 at 279Google Scholar; Birnie and Boyle, op. cit. n. 67, at pp. 1054–1058; Sands, op. cit. n. 75, at pp. 698–699.

85. Decision-Recommendation of the OECD Council Concerning Provision of Information to the Public and Public Participation in Decision-Making Processes Related to the Prevention of, and Response to, Accidents Involving Hazardous Substances, OECD Doc. C(88)85 (Final) (1988), reprinted in 28 ILM (1989) p. 278Google Scholar; Convention on the Transboundary Effects of Industrial Accidents, Helsinki, 17 March 1992, not in force, reprinted in Sands, P. et al, eds., Documents in International Environmental Law, Vol. IIB (Manchester, Manchester University Press 1994) at p. 1351Google Scholar, Art. 9; Convention on Access to Information, Public Participation in Decision-making and Access to Justice in Environmental Matters, Århus 25 June 1998, not in force, reprinted in 38 ILM (1999) p. 517, Art. 5Google Scholar.

86. Guerra and others v. Italy, Judgment of 19 February 1998, ECHR Rep. (1998) Vol. I, para. 60Google Scholar; also McGinley and Egan v. United Kingdom, Judgment of 9 June 1998, ECHR Rep. (1998) Vol. III, para. 101Google Scholar.

87. Simonds, loc. cit. n. 8, at p. 197.

88. In the Corfu Channel Case, supra n. 53, the ICJ based itself on such a ground to establish that Albania had an obligation to warn British warships of a minefield in Albanian territorial waters exposing them to imminent danger. In the case of Military and Paramilitary Activities in and Against Nicaragua (Nicaragua v. US), Judgment of 27 June 1986, ICJ Rep. (1986) p. 14Google Scholar, the Court condemned the US for not having issued warning or notification of the laying of mines in Nicaraguan ports (para. 215).

89. Art. 57(2) AP I. Other provisions that require parties to give warnings include Art. 19 GC IV and Art. 13 AP I (loss of protection of civilian medical units) and Art. 65 AP I (loss of protection of civil defence buildings).

90. Protocol on Prohibitions or Restrictions on the Use of Mines, Booby-Traps and Other Devices as amended on 3 May 1996 (Protocol II to the 1980 Certain Conventional Weapons Convention as amended on 3 May 1996), Art. 3(11).

91. In March 2000, after NATO had furnished partial information on the use of depleted uranium during the conflict, UNEP stated:

‘Whilst welcoming the positive co-operation of NATO, the group, […] concluded that despite the additional information there was still insufficient data available on the exact location of the DU ordnance to comprehensively carry out an objective and scientifically based environmental and human health impact assessment in Kosovo.’

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92. UNEP/UNCHS Balkans Task Force, The Potential Effects on Human Health and the Environment Arising from the Possible Use of Depleted Uranium During the 1999 Kosovo Conflict. A Preliminary Assessment (10 1999) p. 15Google Scholar.